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EC number: 273-066-3 | CAS number: 68937-41-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
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- Flash point
- Auto flammability
- Flammability
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- Stability: thermal, sunlight, metals
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- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
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- Nanomaterial surface chemistry
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- Nanomaterial pour density
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- Endpoint summary
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- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
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- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
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Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 02 September 2010 - 30 September 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study conducted to recognised guidelines
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-E (Determination of the "Ready" Biodegradability - Closed Bottle Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.3110 (Ready Biodegradability)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not applicable. - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Activated sludge, microorganisms from a domestic waste water treatment plant.
Origin:The activated sludge will be supplied from the sewage plant for domestic sewage in Veszprém, Hungary.
Conditioning: The activated sludge used for this study is centrifuged (for 10 min.). Thereafter the supernatant liquid phase is then decanted. The solid material is re-suspended in isotonic saline solution and again centrifuged (for 10 min). This washing procedure is performed in triplicate. An aliquot of the final sludge suspension was then weighed, dried and the ratio of wet sludge to its dry weight determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 3 - 5 g dry material per litre are mixed with test water and then aerated until use. Before use the sludge is filtered through cotton wool. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 2.1 mg/L
- Based on:
- COD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Remarks:
- The oxygen concentrations were measured with oxygen meter with a stirring O2 electrode. Oxygen measurements were performed in duplicate on days 0, 7, 14, 21 and 28.
- Details on study design:
- TEST SYSTEM
The inoculum: Activated sludge, microorganisms from a domestic waste water treatment plant.
Origin: The activated sludge was supplied from the sewage plant for domestic sewage in Veszprém, Hungary.
Conditioning: The activated sludge used for this study was washed by centrifugation (for 10 min.) and the supernatant liquid phase was decanted. The solid material was re-suspended in isotonic saline solution and again centrifuged (for 10 min.). This procedure was repeated twice. An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge to its dry weight was determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 4 g dry material per litre were mixed with test water (see below) and then aerated until use. Before use the sludge was filtered through cotton wool.
TEST UNITS
Type and Size: BOD bottles (300 ml) with special neck and glass stoppers.
Identification: Each test flask was uniquely identified with study code, test group, days of measurement and replicate number.
TEST CONDITIONS
The test was carried out in an incubator and controlled environment room (during the formulation and oxygen measuring) at a temperature of 22 ± 2 deg C according to guideline. The test flasks were placed into an incubator and kept at 20.2-23.6 deg C, in the dark. The temperature was measured on weekdays during the experiment.
The oxygen concentration of test water was 8.4 mg/L at the start of the test.
The pH value of the test water was checked prior study start. The pH of the test water was 7.39.
The test conditions were measured with suitable instruments and documented in the raw data.
PREPARATION OF THE TEST SOLUTIONS
The respective amount of Reofos 65 was weighed in directly to reach the required test item concentration of 2.1 mg/L.
During the performance of the test the test solutions were ultrasonicated for 5 min. to ensure a good dispersion.
The chosen test item concentration was based on the measured chemical oxygen demand (COD): 2.8 ±0.03 mg O2/mg test item and on the performed 14-d preliminary test.
The components were applied in the amounts/volumes following ratio in the test flasks:
1.) Test Item (flasks 1a and 1b)
Based on the chemical oxygen demand (COD) of 2.8 mg O2/mg test item, 7.3 mg of Reofos 65 was thoroughly mixed into 3.46 litres of aqueous test medium (corresponding to 2.1 mg/L test item, respectively a COD of about 5.88 mg O2/L).
2.) Procedure Control: Sodium benzoate (flasks 2a and 2b)
Based on the theoretical oxygen demand (ThODNH4) of Sodium benzoate (1.67 mg O2 per mg) (details on calculation are given in the guidelines), stock solution* corresponding to 12.096 mg of Sodium benzoate was mixed into 3.36 litres of aqueous test medium (corresponding to 3.6 mg/L reference item, respectively a ThODNH4 of about 6.012 mg O2/L).
* The concentration of the stock solution was: 360 mg/L.
3.) Inoculum Control (flasks 3a and 3b)
Only filtered inoculum was added to 3.40 litres of aqueous test medium.
4.) Toxicity Control (flasks 4a and 4b)
7.3 mg of Reofos 65 and reference item stock solution* (34.6 mL) were mixed into 3.46 litres of aqueous test medium corresponding to 2.1 mg/L test item (COD of 5.88 mg O2/L) and 3.6 mg/L reference item (ThODNH4 of 6.012 mg O2/L).
* The concentration of the reference item stock solution was: 360 mg/L.
Microbial inoculum (0.5 ml per litre) was added to each preparation bottle.
COURSE OF THE TEST
Preparation of Test Flasks
Sufficient number of BOD flasks was cleaned with 5 - 10 mL of a wash liquid (2.5 g iodine and 12.5 g potassium iodide per litre of 1 % w/v sulphuric acid) by shaking well to coat the bottle walls. After allowing standing for 15 minutes, the wash liquid was poured off, and the bottles were thoroughly rinsed with tap water and deionised water. Then, the previously described test solutions were filled into the bottles bubble-free until the bottles were completely filled. Then they were tightly closed with glass stopper.
The Test Bottles
The number of test bottles was the follow:
10 bottles containing the test item and inoculum
10 bottles containing the reference item and inoculum (procedure control)
10 bottles containing only inoculum (inoculum control)
10 bottles containing the test item, reference item and inoculum (toxicity control)
Measurement of Temperature
Temperature was measured continuously and registered on weekdays. - Reference substance:
- benzoic acid, sodium salt
- Preliminary study:
- On day 14 biodegradation was 6.8% in case of Reofos 65 pre-test. No further information provided.
- Test performance:
- See below
- Parameter:
- % degradation (O2 consumption)
- Value:
- 17.9
- Sampling time:
- 28 d
- Details on results:
- Under the test conditions the percentage biodegradation of Reofos 65 reached a mean of 17.9 % after 28 days based on the measured COD of the test item.
The test item can therefore be considered to be not ready biodegradable. According to the test guidelines the pass level for ready biodegradability is removal of 60 % ThOD.
According to the test guidelines the test item can be assumed to be not inhibitory at the applied concentration level of 2.1 mg/L on the activated sludge microorganisms because degradation was >25 % within 14 days. - Results with reference substance:
- The reference item Sodium benzoate was sufficiently degraded to a mean of 71.7 % after 14 days, and to a mean of 77.5 % after 28 days of incubation, based on ThODNH4, thus confirming the suitability of the used activated sludge inoculum.
In the toxicity control containing both, the test item and the reference item Sodium benzoate, a mean of 41.6 % biodegradation was noted within 14 days and 42.0 % biodegradation after 28 days of incubation. - Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Under the test conditions the percentage biodegradation of Reofos 65 reached a mean of 17.9 % after 28 days based on the measured COD of the test item. The test item can therefore be considered to be not ready biodegradable
- Executive summary:
The test item Reofos 65 was investigated for its ready biodegradability in a Closed Bottle Test over a period of 28 days. The biodegradation was followed by the oxygen uptake of the microorganisms during exposure. As a reference item Sodium benzoate was tested simultaneously under the same conditions as the test item, and functioned as a procedure control.
The test system was a microbial inoculum of good quality, collected from the sewage plant for domestic sewage. The sludge was washed by centrifugation filtered through cotton wool and aerated until use. Based on the determined dry weight content, the washed sludge suspension contained 4 g dry material per litre.
Under the test conditions the percentage biodegradation of Reofos 65 reached a mean of 17.9 % after 28 days based on the measured COD of the test item.
The test item can therefore be considered to be not ready biodegradable. According to the test guidelines the pass level for ready biodegradability is removal of 60 % ThOD.
The reference item Sodium benzoate was sufficiently degraded to a mean of 71.7 % after 14 days, and to a mean of 77.5 % after 28 days of incubation, based on ThODNH4, thus confirming the suitability of the used activated sludge inoculum.
In the toxicity control containing both, the test item and the reference item Sodium benzoate, a mean of 41.6 % biodegradation was noted within 14 days and 42.0 % biodegradation after 28 days of incubation.
According to the test guidelines the test item can be assumed to be not inhibitory at the applied concentration level of 2.1 mg/L on the activated sludge microorganisms because degradation was >25 % within 14 days.
Reference
Table 2. Dissolved Oxygen Concentrations at Different Time Intervals during the Exposure Period of 28 Days
Treatment |
Concentration |
Flask |
mg O2/L after n days of exposure |
||||
[mg/L] |
No. |
0 |
7 |
14 |
21 |
28 |
|
Test item |
|
1a |
8.2 |
7.6 |
6.9 |
6.6 |
6.1 |
2.1 |
1b |
8.2 |
7.6 |
6.9 |
6.6 |
6.3 |
|
|
mean |
8.20 |
7.60 |
6.90 |
6.60 |
6.20 |
|
Reference item |
|
2a |
8.0 |
3.4 |
3.3 |
2.9 |
2.4 |
3.6 |
2b |
8.1 |
3.3 |
3.1 |
2.7 |
2.5 |
|
|
mean |
8.05 |
3.35 |
3.20 |
2.80 |
2.45 |
|
Inoculum control |
– |
3a |
8.2 |
7.9 |
7.6 |
7.7 |
7.2 |
3b |
8.1 |
7.9 |
7.6 |
7.5 |
7.2 |
||
mean |
8.15 |
7.90 |
7.60 |
7.60 |
7.20 |
||
Toxicity control |
Test item: 2.1 |
4a |
8.2 |
3.0 |
2.4 |
2.1 |
2.0 |
4b |
8.2 |
3.2 |
2.3 |
2.1 |
1.8 |
||
mean |
8.20 |
3.10 |
2.35 |
2.10 |
1.90 |
Table 3. Oxygen Depletion at Different Time Intervals during the Exposure Period of 28 Days
Treatment |
Concentration |
Flask |
mg O2/L after n days of exposure |
|||
[mg/L] |
No. |
7 |
14 |
21 |
28 |
|
Test item |
2.1 |
1a |
0.35 |
0.75 |
1.05 |
1.15 |
1b |
0.35 |
0.75 |
1.05 |
0.95 |
||
Reference item |
3.6 |
2a |
4.35 |
4.15 |
4.55 |
4.65 |
2b |
4.55 |
4.45 |
4.85 |
4.65 |
||
Toxicity control |
Test item: 2.1 |
4a |
4.95 |
5.25 |
5.55 |
5.25 |
4b |
4.75 |
5.35 |
5.55 |
5.45 |
oxygen depletion : (mt0 - mtx) - (mbo - mbx), where:
mt0 : oxygen concentration (mg/L) of test group on day 0 (1a, 2a, 4a and 1b, 2b, 4b from Table 2)
mtx: oxygen concentration (mg/L) of test group on day x (1a, 2a, 4a and 1b, 2b, 4b from Table 2)
mb0: oxygen concentration (mg/L) of inoculum blank on day 0 (mean of 3a and 3b from Table 2)
mbx: oxygen concentration (mg/L) of inoculum blank on day x (mean of 3a and 3b from Table 2)
Table 4. BOD at Different Time Intervals during the Exposure Period of 28 Days
Treatment |
Concentration |
Flask |
BOD after n days of exposure |
|||
[mg/L] |
No. |
7 |
14 |
21 |
28 |
|
Test item |
2.1 |
1a |
0.17 |
0.36 |
0.50 |
0.55 |
1b |
0.17 |
0.36 |
0.50 |
0.45 |
||
Reference item |
3.6 |
2a |
1.21 |
1.15 |
1.26 |
1.29 |
2b |
1.26 |
1.24 |
1.35 |
1.29 |
||
Toxicity control |
Test item: 2.1 |
4a |
0.87 |
0.92 |
0.97 |
0.92 |
4b |
0.83 |
0.94 |
0.97 |
0.96 |
BOD = = mg O2/mg T.i and/or
where:
T.i. = test item
R.i. = reference item
i.control = inoculum control
Table 5. Percentage Biodegradation at Different Time Intervals during the Exposure Period of 28 Days
Treatment |
Concentration |
Flask |
Percent of biodegradation after n days of exposure |
|||
|
[mg/L] |
No. |
7 |
14 |
21 |
28 |
Test item |
|
1a |
6.0 |
12.8 |
17.9 |
19.6 |
2.1 |
1b |
6.0 |
12.8 |
17.9 |
16.2 |
|
|
mean |
6.0 |
12.8 |
17.9 |
17.9 |
|
Reference item |
|
2a |
72.5 |
69.2 |
75.8 |
77.5 |
3.6 |
2b |
75.8 |
74.2 |
80.8 |
77.5 |
|
|
mean |
74.2 |
71.7 |
78.3 |
77.5 |
|
Toxicity control |
Test item: 2.1 |
4a |
38.9 |
41.2 |
43.6 |
41.2 |
4b |
37.3 |
42.0 |
43.6 |
42.8 |
||
mean |
38.1 |
41.6 |
43.6 |
42.0 |
Biodegradation % =
where:
T.i. = test item
R.i. = reference item
i.control = inoculum control
COD of test item = 2.80 ± 0.03 mg O2/mg test item
ThODNH4 of reference item = 1.67 mg O2/mg reference item
The biodegradation in the toxicity control was calculated according to the following formula:
Description of key information
Biodegrdation is discussed.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
Under the test conditions the percentage biodegradation of Reofos 65 reached a mean of 17.9 % after 28 days based on the measured COD of the test item. The test item can therefore be considered to be not ready biodegradable. Biodegradation testing is currently under investigation as part of Draft Decision On Substance Evaluation under Article 46 of Regulation (EC) No 1907/2006 (REACH) relating to SEV-D-2114548209-44-01/D. Further works relating to this endpoint will be considered once this exercise is completed.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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